My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0001629
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
C
>
CHEROKEE
>
16
>
2900 - Site Mitigation Program
>
PR0522479
>
ARCHIVED REPORTS XR0001629
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/17/2019 3:43:00 PM
Creation date
5/17/2019 2:13:45 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001629
RECORD_ID
PR0522479
PE
2957
FACILITY_ID
FA0015299
FACILITY_NAME
GEWEKE LAND DEVELOPMENT & MARKETING
STREET_NUMBER
16
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04323013
CURRENT_STATUS
01
SITE_LOCATION
16 S CHEROKEE LN
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\wng
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
81
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
the plumes suggests that hydrocarbons have migrated preferentially <br /> along high-permeability axial zones of the channel deposits, rather <br /> than directly down the groundwater gradient, which is oriented <br /> north-south rather than northeast-southwest. It appears that the <br /> permeability to hydrocarbons is less than the permeability to <br />' uncontaminated groundwater, thereby slowing the southward migration <br /> of contaminants. <br /> 5. 0 REMEDIATION ALTERNATIVES <br /> When considering remediation alternatives for both soil and <br /> I groundwater, several conditions must be met. It is important to <br /> employ remedial methods that are effective, affordable, and <br /> environmentally safe. Other factors that must be considered include <br /> on-site safety and minimizing disruptions of the normal operations <br /> of the site. <br /> 5 . 1 Soil Remediation <br /> To remediate the soil at the site, three alternatives were <br /> considered: excavation and disposal or on-site treatment; in-situ <br /> vapor extraction; and in-situ bioremediation. The following <br /> sections briefly discuss the theory, feasibility, cost and <br /> estimated time of completion for each method. <br /> 5 . 1. 1 Excavation <br /> Excavation is a fast and effective method of site remediation where <br /> the contamination is shallow and distant from sensitive features. <br /> Once the contaminated soil has been removed from the excavation, it <br /> can be treated on-site or transported to an appropriate landfill <br /> facility. However, if transported, liability for the soil usually <br /> remains with the generator. Excavation is usually not feasible <br /> beyond a depth of 30 to 40 feet. <br /> Assuming that excavation to a depth of 35 feet could be undertaken, <br /> between 30 and 40% of the contaminated soil at the site could be <br /> removed for treatment or disposal. Due to the lateral spreading of <br /> soil contamination below 30 feet, more than 50% of the <br /> contamination is not accessible by normal excavation methods. The <br /> highest concentrations of hydrocarbons, at a depth of 20 to 25 <br /> feet, would be removed, but the secondary cell at 40 to 50 feet <br /> would probably be left in the ground. Excavation would probably <br /> I require several days to a few weeks, causing significant <br /> inconvenience to the property owner. GeoAudit does not regard <br /> excavation as a viable option for the site. <br /> 6 <br />
The URL can be used to link to this page
Your browser does not support the video tag.